Removal of Saline Water due to Road Salt Applications from Columns of Two Types of Sand by Rainwater Infiltration: Laboratory Experiments and Model Simulations

• Published in: Water, air, and soil pollution air, and soil pollution, 2019-12, Vol.230 (12), Article 305
• Main Authors: Higashino, Makoto, Stefan, Heinz G, Aso, Daiki
• Format: Article
• Language: English
• Subjects: Atmospheric Protection/Air Quality Control/Air Pollution; Clay; Climate Change/Climate Change Impacts; Computer simulation; Earth and Environmental Science; Effluents; Electric properties; Electrochemistry; Environment; Environmental monitoring; Experiments; Grain size; Granite; Gravel; Hydraulics; Hydrogeology; Ice; Infiltration; Laboratories; Local transit; Mass transport; Pores; Rain; Rain water; Rain-water (Water-supply); Road salt; Roads & highways; Saline water; Salt; Salts; Sand; Sand, gravel and stone industry; Silt; Simulation; Soil columns; Soil Science & Conservation; Soils; Technology application; Water quality; Water Quality/Water Pollution
• ISSN: 0049-6979; 1573-2932
• DOI: 10.1007/s11270-019-4337-0

Mass transport and residence time of saline water from road salt applications in soil columns composed of Toyoura sand and weathered granite sand were investigated by simulations and in laboratory experiments. Both are sands found in Japan, especially the weathered granite sand. The Toyoura sand has a fairly uniform particle size of 0.1 to 0.4 mm diameter, and a saturated hydraulic conductivity K s = 0.0296 cm/s, while the weathered granite sand used consisted of 13% fine materials (silt and clay) and 87% coarse materials (sand and gravel) with a saturated hydraulic conductivity K s = 0.00393 cm/s. A model was developed to simulate rinsing of brine from a soil column. Assuming a steady, homogeneous flow induced by rainwater infiltration into the soil column, the model was found to match the experimental results for Toyoura sand very well. The normalized salt concentration in the effluent from the 40 cm tall soil column remained constant until about t = 500 s; the concentration then decreased with time quickly and, finally, approached zero. For the weathered granite sand, however, the salt concentrations in the effluent simulated by the model with assumption of homogeneous flow are inconsistent with the experimental data collected. A substantial delay occurs in mass transport of salt from the column, which is different from the Toyoura sand. The delay is attributed to shifts in “active” and “inactive pores” created in the soil due to fine particles such as silt and clay. The proportion of “active pores” and “inactive pores” is not constant but variable with time due to physical and/or electrochemical processes such as pore-size distributions and salt depletion in the soil. A modified model presented, using a time-variable active pore parameter k(t), can reproduce the experimental results for salt mass left in the soil better.